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5.2 The environmental assessment—LCA             103
            2005; Funazaki et al., 2003; Park et al., 2003; Chevalier et al., 2003; Shiels et al., 2002). The
            main content aims to:

            (1) formulate environmental policy and international management system, coordinate the
               regional or global environmental problems, improve and protect environment by
               standard ways, and satisfy the needs of sustainable development of economy;
            (2) establish environmental product standard and implement ecolabelling plan;
            (3) formulate corresponding tax, credit, investment, and environmental protection policy,
               and accelerate the development of the industry of waste recovery and recycling;
            (4) optimize energy, transportation, and waste management solutions of government,
               minimize the environmental load and economic cost of the economic system; and
            (5) provide the public with information about the related products and raw materials,
               improve ecological consumption benchmarks, and advocate green and sustainable
               consumption.

            5.2.4 Limitation
              Though the technical framework and analysis features of an LCA have also been widely
            accepted and understood, there is no consensus on the specific operation. Therefore, LCA
            faces many complications, as exhibited in the definition of system boundary, the definition
            of the impact categories, the choice of the impact evaluation models, and so on. As far as eval-
            uation methods are concerned, some defects remain in current impact evaluation models and
            integration methods.

            5.2.4.1 Objective problems
              It is almost impossible for life cycle assessment to avoid the influence of subjective factors,
            which is determined by the understanding of the LCA method, the knowledge of the system
            evaluated, the knowledge background, and the value judgment of the executors of an LCA
            (Huijbregts, 1998; Owens, 1996). For example, in one respect, the choice of the system bound-
            ary depends on the cognition degree of the object of the study and the predetermined research
            target. In another aspect, when quantificationally evaluating an impact type, several kinds of
            models can be used to determine the effect. Different models can offer different results, some
            of which can be measured in orders of magnitude. Thus, artificial selections of impact assess-
            ment models make the evaluation results subjective.

            5.2.4.2 Limitations of information and data
              ForLCA,thelimitationsofinformationanddataareoneofthemajorhindrances(Ciroth,2004;
            Rossetal.,2002).Thishindranceappearsintwoaspects:lackofinformationwhichcanbeusedas
            influencecategorybasis,andlackofinformationanddatafromeachstageoftheLCA.Itisusually
            hard to obtain the related data and the data gained is of low quality. The typical production pro-
            cess or the mean level are adopted as the substitutes. The data may be estimated by empirical
            formulas (or experience judgment); this means that the data may be inaccurate and the error
            maybebigger,whichcouldbemisleading.Itisalsonoteasytosolvetheproblemsabove.Inorder
            to solve the problems, the mining industry, the raw material production industry, and the prod-
            uct manufacturing industry should work together, effectively.
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